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1.
以青鳉鱼和大型溞为代表性水生生物,研究三唑酮对其不同测试终点的慢性毒性效应.结果显示,以生存、生长、繁殖为测试终点,青鳉鱼的NOEC分别为76,60,5μg/L,基于大型溞蜕皮次数、生长和繁殖的NOEC分别为25,100,200μg/L.由此可见,青鳉鱼比大型溞对三唑酮的毒性更敏感.比较不同测试终点,青鳉鱼的繁殖类指标最敏感,其次是生长、生存;相比大型溞的繁殖以及幼溞的生长,其幼溞的蜕皮次数指标更为敏感.因此,低剂量长期暴露下三唑酮会对水生生物的繁殖能力造成一定的损伤,评价其水生态安全应全面考虑不同生物种群的不同测试终点,尤其是鱼类繁殖毒性效应.  相似文献   
2.
多种污染物混合特别是低浓度下的混合对生物的联合毒性是生态毒理学研究的热点之一。选择了3类污染物苯酚、间甲基苯酚、苯胺、对硝基苯胺、硝酸铅,采用美国微板光度计测定了它们对发光菌青海弧菌-Q67(Vibrio-qinghaiensis sp.-Q67)的单一及联合毒性。应用非线性拟合技术模拟了这5种物质及其混合物的剂量-效应曲线,硝酸铅可用Logit模型模拟,其它4个物质能用Weibull模型准确描述,所有拟合相关系数在0.98以上,均方根误差在0.02以下。根据纯物质的EC50值,获得这5个物质的毒性强弱顺序:硝酸铅〉对硝基苯胺间甲基苯酚苯酚苯胺。混合实验设计了各物质在EC50、EC1、无观察效应浓度(no observed effect concentration,NOEC)比例的混合。用浓度加和(dose addition,DA)和独立作用模型(independent action,IA)对混合物毒性进行预测。IA基本准确预测了这5个物质在各自EC50混合的毒性。DA与IA模型都稍微过高地预测了以EC1及NOEC浓度比例混合的联合毒性,但都在毒理学实验容许的范围之内。这5个物质以NOEC混合时对测试生物Q67没有产生明显毒性,但是还不能判定这些物质在此浓度下混合是安全的。污染物在各自的NOEC浓度下混合是否对其它生物有潜在的威胁还需更多毒理学实验支持。  相似文献   
3.
Jin X  Zha J  Xu Y  Giesy JP  Richardson KL  Wang Z 《Chemosphere》2012,86(1):17-23
2,4,6-Trichlorophenol (2,4,6-TCP) is a common chemical intermediate and a by-product of water chlorination and combustion processes, and is a priority pollutant of the aquatic environment in many countries. Although information on the toxicity of 2,4,6-TCP is available, there is a lack of information on the predicted no-effect concentration (PNEC) of 2,4,6-TCP, mainly due to the shortage of chronic and site-specific toxicity data. In the present study, acute and sub-chronic toxicity of 2,4,6-TCP on six different resident Chinese aquatic species were determined. PNEC values were calculated and compared by use of two approaches: assessment factor (AF) and species sensitivity distribution (SSD). Values for acute toxicity ranged from 1.1 mg L−1 (Plagiognathops microlepis) to 42 mg L−1 (Corbicula fluminea) and the sub-chronic no observed effect concentrations (NOECs) ranged from 0.05 mg L−1 (Mylopharyngodon piceus) to 2.0 mg L−1 (C. fluminea). PNECs obtained by the assessment factor approach with acute (AF = 1000, 0.001 mg L−1) or chronic (AF = 10, 0.005 mg L−1) toxicity data were one order of magnitude less than those from SSD methods (0.057 mg L−1). PNEC values calculated using SSD methods with a 50% certainty for 2,4,6-TCP was less than those obtained by use of the USEPA recommend final chronic value (FCV) method (0.097 mg L−1) and the one obtained by use of the USEPA recommend acute-to-chronic (ACR) methods (0.073 mg L−1). PNECs derived using AF methods were more protective and conservative than that derived using SSD methods.  相似文献   
4.
丙烯酰胺对大型(Daphniamagna)的急性试验表明,丙烯酰胺对大型的24h LC50、48h LC50值分别为173.21和89.59mg·L-1。21d生活周期试验结果表明,大型的生殖指标是对该种化合物最为敏感的慢性毒性参数。丙烯酰胺对大型生殖的无可见效应浓度(NOEC)为1.56mg·L-1,最低可见效应浓度(LOEC)为3.13mg·L-1,并据此计算出该毒物的最大允许浓度(MATC)为2.47mg·L-1。  相似文献   
5.
多种污染物混合特别是低浓度下的混合对生物的联合毒性是生态毒理学研究的热点之一。选择了3类污染物苯酚、间甲基苯酚、苯胺、对硝基苯胺、硝酸铅,采用美国微板光度计测定了它们对发光菌青海弧菌.Q67(Vibrio-qinghaiensissp-Q67)的单一及联合毒性。应用非线性拟合技术模拟了这5种物质及其混合物的剂量.效应曲线,硝酸铅可用Logit模型模拟,其它4个物质能用Weibull模型准确描述,所有拟合相关系数在0.98以上,均方根误差在O.02以下。根据纯物质的EC50值,获得这5个物质的毒性强弱顺序:硝酸铅〉对硝基苯胺〉间甲基苯酚〉苯酚〉苯胺。混合实验设计了各物质在EC50、EC1、无观察效应浓度(noobserved effectcon centration,NOEC)比例的混合。用浓度加和(doseaddition,DA)和独立作用模型(independentaction,IA)对混合物毒性进行预测。IA基本准确预测了这5个物质在各自EC50混合的毒性。DA与队模型都稍微过高地预测了以EC。及NOEC浓度比例混合的联合毒性,但都在毒理学实验容许的范围之内。这5个物质以NOEC混合时对测试生物Q67没有产生明显毒性,但是还不能判定这些物质在此浓度下混合是安全的。污染物在各自的NOEC浓度下混合是否对其它生物有潜在的威胁还需更多毒理学实验支持。  相似文献   
6.
毒性数据是对化学品进行环境风险评价的基础,慢性毒性数据更能真实的反映毒物对水生生物生长、繁殖及生理功能产生的影响。本文采用细菌生长抑制实验,测定了17种卤代苯对长江水中混合细菌的慢性毒性,得到-lgNOEC值,毒性范围在4.27(氯苯)~5.22(1,2,4-三氯苯)之间。选用量化参数对毒性数据进行定量结构活性关系(QSAR)研究,结果表明,卤代苯对江水细菌的慢性毒性主要与化合物分子的空间大小有关,量化参数范德华面积(SVdW)及分子生成热(Hf)能够很好的描述卤代苯对江水细菌的慢性毒性。  相似文献   
7.
8.
Dang Z  Traas T  Vermeire T 《Chemosphere》2011,85(10):1592-1603
In a fish testing strategy, positive results of the fish short term reproduction assay (FSTR), often trigger a definitive test like the fish sexual development test (FSDT) or the fish full life cycle test (FFLC), entailing ethical and economic problems. This study analysed 137 studies encompassing 35 chemicals with different modes of actions (MOAs). Variability is quantified for MOA endpoints vitellogenin (VTG) and secondary sex characteristics (SSCs) as well as for apical endpoints. Two MOA endpoints could indicate estrogenic, anti-estrogenic, androgenic, anti-androgenic and steroidogenesis activities. Great variability, however, has been observed for chemicals with anti-androgenic and steroidogenesis activities, suggesting that TG229/230 may not be sensitive enough to detect these types of chemicals and may produce false negatives. Changes in apical endpoints like fecundity are not limited to endocrine disrupting chemicals (EDCs). Non-EDCs could induce the similar effects on these apical endpoints. If elucidating MOA is needed, targeted in vitro MOA tests are suggested. Positive in vitro MOA results trigger a definitive test, which could be used for confirmation of the MOA in vivo and for deriving a no observed effect concentration (NOEC). Based on positive MOA results of TG229, a definitive test such as the FSDT or the FFLC is still needed, because the current TG229 has limitation on the derivation of a NOEC. An extended TG229 with more power to detect reproduction effects, as recently proposed in the OECD test guideline program, would improve the possibility to derive a NOEC and increase its usefulness in risk assessment.  相似文献   
9.
镉对泥鳅幼鱼的急性和亚急性毒性研究   总被引:13,自引:0,他引:13  
在实验条件下研究了镉对泥鳅幼鱼的急性和亚急性毒性。试验从刚孵出的幼鱼开始,采用静水换水法。亚急性试验历时20d。镉对泥鳅幼鱼24、48h的LC50值分别为1.22、0.85mg/L。亚急性试验中,镉对泥鳅幼鱼存活有明显影响的可观察效应浓度(LOEC)最低是O.16mg/L;根据对幼鱼现存量的影响,镉对泥鳅的最低可观察效应浓度为0.08mg/L,而无可观察效应浓度(NOEC)为0.04mg/L。  相似文献   
10.
The fate and effect of nanomaterials in the environment is of paramount importance towards the technological application of the materials. This work shows the ecotoxicological potential of polyaniline (PANI) nanofibers in the larvae Rhinella arenarum by means of AMPHITOX test. Acute toxicity of PANI nanofibers towards embryos of the common South American toad R. arenarum (Anura: bufonidae) was evaluated in the premetamorphosis (stage 25) larvae. The exposure of R. arenarum larvae to at dose of 150, 250 and 400 mg L−1 resulted in 100% viability within 96 h exposure. The embryos at 2-4 blastomers stage (early life stage teratogenic test) revealed that embryos were not killed and no teratogenic effects were observed when embryos were incubated with PANI nanofibers (150 and 250 mg L−1), while only a growth retardation of embryos was induced at levels of 250 mg PANI nanofibers L−1. On the other hand, at 400 mg L−1 concentration, a reduction in the body length of larvae and tail malformation was observed. This results suggest that a concentration-dependent toxicity is operative, typified by phenotypes that had abnormal body axes. The presence of PANI nanofibers in gut contents and its excretion by larval stages of R. arenarum was confirmed by UV-visible spectroscopy.  相似文献   
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